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Fig. 13 in Breeding Bird Assemblage In A Mosaic Of Urbanized Habitats In A Cenral European City
Fig. 13 Distribution of occupied territories of Fig. 14. Distribution of occupied territories of Fringilla coelebs. Carduelis carduelis.
Supplementary material 1 from: Chen D, van Kleunen M (2022) Competitive effects of plant invaders on and their responses to native species assemblages change over time. NeoBiota 73: 19-37. https://doi.org/10.3897/neobiota.73.80410
Table S1–S6, Figs S1–S3
Re-surveys reveal biotic homogenization of Orthoptera assemblages as a consequence of environmental change
<p>Aim: Biodiversity loss is a major global challenge. While population trends of vertebrates are well documented, insect declines have not been sufficiently studied and their drivers are still not fully understood. This inhibits the implementation of sensible conservation action. Repeating historical surveys can help to reveal the patterns and drivers of insect declines.</p> <p>Location: Central Europe</p> <p>Time period: 2018 to 2020</p> <p>Methods: We resurveyed 199 study sites in which Orthoptera assemblages had been recorded between 1986 and 1999.</p> <p>Results: Our results show a significant increase in species per site (α-diversity), but simultaneously a homogenization of Orthoptera assemblages (decreasing Sorensen's β-diversity). Highly mobile species significantly increased in site occupancy compared to species with low mobility. Some Orthoptera species showed significant altitudinal range shifts, including species with positive trends (i.e. expansion to higher altitudes) and negative trends (i.e. extinction at lower altitudes). Abandonment of extensively used grassland sites and the associated afforestation had negative effects on Orthoptera, underlining the importance of extensive grassland management. Protected areas had a high efficacy for conservation as trends in site occupancy were generally more positive in protected areas than in unprotected sites.</p> <p>Main conclusions: Our results provide insights into the patterns and drivers of orthopteran assemblage turnover, including major effects of agricultural land use change and climate change. These results are essential for implementing or adapting conservation action, as they show that traditional land use practices and reduction of nitrogen input are important to preserve Orthoptera. Insect monitoring is crucial for understanding global and regional insect population trends and for preventing species extinctions. It is therefore critical to repeat historical surveys in order to understand global biodiversity change and implement the necessary actions.</p>
Features of visitors in the context of island-based assemblage and foraging profile related to Avicennia species from Indian Sundarban mangroves
<p>This dataset demonstrates the assemblage pattern and foraging behavior of insect flower visitors on the <em>Avicennia officinalis </em>and <em>Avicennia marina</em> plant from the mangroves of Indian Sundarban.</p>
Text-fig. 6. Quercus sp. Red Oak, UF 279-24550. a, b: Wood semi-ring-porous to diffuse-porous; vessels exclusively solitary; thinwalled tyloses in wide vessels; diffuse, diffuse-in-aggregates axial parenchyma; rays of two distinct sizes. TS. c: Rays of two distinct sizes, TLS. d: Vessel-vasicentric tracheid pitting, RLS. e: Vessel-ray parenchyma pitting with reduced borders, vertically elongate, RLS. f: Narrow rays 1-2 cells wide, TLS. g: Ray composed of procumbent cells, RLS. Scale bars: 200 µm in a, b, c; 50 µm in d, f, g; 20 µm in e. in A Diverse Assemblage Of Late Eocene Woods From Oregon, Western Usa
Text-fig. 6. Quercus sp. Red Oak, UF 279-24550. a, b: Wood semi-ring-porous to diffuse-porous; vessels exclusively solitary; thinwalled tyloses in wide vessels; diffuse, diffuse-in-aggregates axial parenchyma; rays of two distinct sizes. TS. c: Rays of two distinct sizes, TLS. d: Vessel-vasicentric tracheid pitting, RLS. e: Vessel-ray parenchyma pitting with reduced borders, vertically elongate, RLS. f: Narrow rays 1-2 cells wide, TLS. g: Ray composed of procumbent cells, RLS. Scale bars: 200 µm in a, b, c; 50 µm in d, f, g; 20 µm in e.
Figures 2-9 from: Silva GL, Metzelthin MH, Da-Costa T, Rocha MS, Silva DE, Ferla NJ, Silva OS (2017) Responses of water mite assemblages (Acari) to environmental parameters at irrigated rice cultivation fields and native lakes. Zoologia 34: 1-8. https://doi.org/10.3897/zoologia.34.e19988
Figures 2-9 View of the study sites: (2) Detailed view of the rice-water samples, (3) Rice area 1 – R1, (4) Rice area 2 – R2, (5) Rice area 3 – R3, (6) Rice area 4 – R4, (7) Lake 1 – L1, (8) Lake 2 – L2, (9) Lake 3 – L3.
Figures 12-13 from: Silva GL, Metzelthin MH, Da-Costa T, Rocha MS, Silva DE, Ferla NJ, Silva OS (2017) Responses of water mite assemblages (Acari) to environmental parameters at irrigated rice cultivation fields and native lakes. Zoologia 34: 1-8. https://doi.org/10.3897/zoologia.34.e19988
Figures 12-13 Ordination diagram (first two axes) of Non-Metric Multidimensional Scaling (NMDS) using (12) Bray-Curtis and (13) Jaccard indexes with Envfit function for the evaluated environments. (▲ Lake 1, ■ Lake 2 and 3, ● Rice Area). Stress: 0.15.
Figures 10-11 from: Silva GL, Metzelthin MH, Da-Costa T, Rocha MS, Silva DE, Ferla NJ, Silva OS (2017) Responses of water mite assemblages (Acari) to environmental parameters at irrigated rice cultivation fields and native lakes. Zoologia 34: 1-8. https://doi.org/10.3897/zoologia.34.e19988
Figures 10-11 Abundance and richness of mites in rice areas cultivation and native lakes: (10) abundance adults (± SD) (Log10 X+1); (11) richness (± SD) (Log10 X+1). Different letters indicate significant differences, Tukey test, p < 0.05.
Figure 8 from: Gray R, Strine CT (2017) Herpetofaunal assemblages of a lowland broadleaf forest, an overgrown orchard forest and a lime orchard in Stann Creek, Belize. ZooKeys 707: 131-165. https://doi.org/10.3897/zookeys.707.14029
Figure 8 - Rarefaction curves displaying sample based species richness and diversity for amphibian and reptiles captured in each habitat type.
Figure 4 from: Gray R, Strine CT (2017) Herpetofaunal assemblages of a lowland broadleaf forest, an overgrown orchard forest and a lime orchard in Stann Creek, Belize. ZooKeys 707: 131-165. https://doi.org/10.3897/zookeys.707.14029
Figure 4 - Bar graphs exhibiting species capture diversity and richness in reptiles and amphibians before and after Hurricane Earl.
Figure 2 from: Gray R, Strine CT (2017) Herpetofaunal assemblages of a lowland broadleaf forest, an overgrown orchard forest and a lime orchard in Stann Creek, Belize. ZooKeys 707: 131-165. https://doi.org/10.3897/zookeys.707.14029
Figure 2 - Toucan Ridge Ecology and Education Society (TREES) habitat map showing the Heavily Manicured Orchard (HMO), Overgrown Orchard Forest (OGF), Lowland Broadleaf Forest (LBF), and Overgrown Orchard Riparian Forest (OGR) areas, including locations where trapping arrays were set. Additionally, the map indicates the large stream which runs through the property and smaller streams that can be found throughout the forested areas.
Figure 1 from: Gray R, Strine CT (2017) Herpetofaunal assemblages of a lowland broadleaf forest, an overgrown orchard forest and a lime orchard in Stann Creek, Belize. ZooKeys 707: 131-165. https://doi.org/10.3897/zookeys.707.14029
Figure 1 - Stann Creek District, Belize, with the location of Toucan Ridge Ecology and Education Society (TREES).
Figure 5 from: Gray R, Strine CT (2017) Herpetofaunal assemblages of a lowland broadleaf forest, an overgrown orchard forest and a lime orchard in Stann Creek, Belize. ZooKeys 707: 131-165. https://doi.org/10.3897/zookeys.707.14029
Figure 5 - Boxplots of reptile and amphibian capture rates by trap night in the Heavily Manicured Orchard (HMO), Overgrown Orchard Forest (OGF), Overgrown Orchard/Riparian Forest, (OGR) and Lowland Broadleaf Forest (LBF).
Figure 3 from: Gray R, Strine CT (2017) Herpetofaunal assemblages of a lowland broadleaf forest, an overgrown orchard forest and a lime orchard in Stann Creek, Belize. ZooKeys 707: 131-165. https://doi.org/10.3897/zookeys.707.14029
Figure 3 - Boxplots representing the values (%) of canopy cover in each habitat taken before and after Hurricane Earl.
Figure 7 from: Gray R, Strine CT (2017) Herpetofaunal assemblages of a lowland broadleaf forest, an overgrown orchard forest and a lime orchard in Stann Creek, Belize. ZooKeys 707: 131-165. https://doi.org/10.3897/zookeys.707.14029
Figure 7 - Reptile rank abundance curves (using the logarithm of abundances) for the Heavily Manicured Orchard (HMO), Overgrown Orchard Forest (OGF), Overgrown Orchard Riparian Forest (OGR) and Lowland Broadleaf Forest (LBF) study sites; the three most abundant species captured in each site is labeled in each of the four plots.
Figure 6 from: Gray R, Strine CT (2017) Herpetofaunal assemblages of a lowland broadleaf forest, an overgrown orchard forest and a lime orchard in Stann Creek, Belize. ZooKeys 707: 131-165. https://doi.org/10.3897/zookeys.707.14029
Figure 6 - Amphibian rank abundance curves (using the logarithm of abundances) for the Heavily Manicured Orchard (HMO), Overgrown Orchard Forest (OGF), Overgrown Orchard Riparian Forest (OGR) and Lowland Broadleaf Forest (LBF); the three most abundant species captured in each site is labeled in each of the four plots.
DATASET Temporal shifts in algal and fish assemblages following the introduction of herbivorous species in coral reef patches (Bora Bora Island)
<p>Dataset suporting the study of fish succession in Bora Bora</p>
Fig. 4. Representative batoid chondrichthyan teeth from the J&M in New Late Cretaceous microvertebrate assemblage from the Campanian-Maastrichtian Williams Fork Formation, northwestern Colorado, USA, and its paleoenvironmental implications
Fig. 4. Representative batoid chondrichthyan teeth from the J&M site, Colorado, USA, Williams Fork Formation, Upper Cretaceous. A, B. Myledaphus bipartitus Cope, 1876. A. MWC 8887, tooth crown and root in mesial (A1), labial (A2), and occlusal (A3) views. B. MWC 9591, tooth crown and root in mesial (B1), labial (B2), and occlusal (B3) views. C, D. Pseudomyledaphus sp. C. MWC 9589, tooth crown and root in mesial (C1) and occlusal (C2) views. D. MWC 9590, tooth crown and root in mesial (D1) and occlusal (D2) views. E, F. Cristomylus sp. E. MWC 8886, tooth crown in mesial (E1) and occlusal (E2) views. F. MWC 9588, tooth crown in mesial (F1) and occlusal (F2) views.
Fig. 2 in New Late Cretaceous microvertebrate assemblage from the Campanian-Maastrichtian Williams Fork Formation, northwestern Colorado, USA, and its paleoenvironmental implications
Fig. 2. Stratigraphy of the J&M site within the Williams Fork Formation. A. Regional Upper Cretaceous stratigraphy. B. Generalized stratigraphic section of the Williams Fork Formation west of Rangely (after Noll 1988). C. Stratigraphic section of Williams Fork Formation strata exposed at the J&M site, showing the stratigraphic position of the locality in Noll's (1988) "sandstone C". Width of stratigraphic units mimics the local weathering profile. Shading on unit 3B indicates a darker color than mudstones A and C. A detailed description of the J&M site stratigraphy is provided in the SOM: table S1 (Supplementary Online Material available at http://app.pan.pl/SOM/app67-Brand_etal_SOM.pdf).
Fig. 9 in Palaeoecology of tropical marine invertebrate assemblages from the Late Triassic of Misurina, Dolomites, Italy
Fig. 9. Neritariid gastropods Dentineritaria neritina (Münster, 1841) from Lago Antorno (A) and Misurina Landslide (B, C), northern Italy, Cassian Formation, Carnian, Upper Triassic. A. PZO 12801, in apertural (A1) and apical (A2) views; A3, end of smooth larval shell well visible in oblique lateral view. B. PZO 12683, in apertural (B1) and abapertural (B2) views. C. PZO 12684 in apical view.
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Allen Brain Atlas
Allen Brain Atlas is an Allen Institute collection of brain map atlases, datasets, APIs, and analysis tools covering mouse, human, and non-human primate brain resources.
Annotated Behaviour and Observability Dataset (ABODe)
ABODe is a University of Edinburgh DataShare dataset for behavior classification in group-housed mice using home-cage video, identities, bounding boxes, ground-plate positions, and annotator labels.
DANDI Archive for NWB datasets
DANDI is a BRAIN Initiative archive for publishing and sharing neurophysiology data, including electrophysiology, optophysiology, and behavioral data packaged as NWB and related standards.
International Brain Laboratory public data
The International Brain Laboratory public data releases expose standardized mouse decision-making experiments, including Neuropixels recordings, widefield calcium imaging, behavior, and session metadata accessed through the ONE API.
OpenNeuro
OpenNeuro is a free, open platform for sharing neuroimaging datasets, with public search, dataset pages, and download paths for web, S3, DataLad, and the OpenNeuro CLI.